Table 3.
2000 U.S. Census |
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Response variable Modelb | Mean distance to CSO (m) | Mean distance to catch basin (m) | Mean tree cover (%) | Mean elevation (m) | Percent houses 1950s–1960s | Median household income (U.S. dollars) | No. dead corvids | Constant | AIC | ΔAIC | ωic |
Human WNV incidence | |||||||||||
1 | −6E–5** | — | −0.0018 | — | 0.0276* | −1E–5* | −0.0362 | 3.60* | 309.0 | 0.0 | 0.817 |
2 | −6E–5** | 5E–5 | −0.0012 | −0.0018 | 0.0287* | −2E–5* | −0.032 | 4.13* | 313.1 | 4.1 | 0.105 |
3 | −8E–5* | 3E–5 | — | — | — | — | −0.117* | 2.65* | 314.8 | 5.8 | 0.04 |
4 | — | — | — | — | 0.0381* | −2E–5* | — | 3.58* | 316.8 | 7.8 | 0.02 |
5 | — | — | −0.020* | −0.0035 | — | — | — | 3.75* | 316.9 | 7.9 | 0.02 |
∑ωi | 9.7E–1c | 0.0 | 0.02 | 0.0 | 0.94 | 9.2E–1 | 0.04 | ||||
WNV-positive corvid death ratio | |||||||||||
1 | −6E–4* | — | 0.194* | — | 0.1095 | 1.0E–5* | — | 4.26* | 707.0 | 0 | 0.913 |
2 | −6E–4* | 2E–5 | 0.215* | −0.0159 | 0.1023 | −6.0E–5 | — | 10.46* | 711.7 | 4.7 | 0.09 |
3 | — | — | — | — | 0.186* | 1.4E–4* | — | 1.19 | 728.2 | 21.2 | 0.00 |
4 | — | — | 0.172* | −0.0017 | — | — | — | 4.83 | 728.4 | 21.4 | 0.00 |
5 | −3E–4 | −1E–5 | — | — | — | — | — | 11.61* | 739.9 | 32.9 | 0.00 |
∑ωi | 1.0 | 0.0 | 1.0 | 0.0 | 0.0 | 9.1E–1 |
Results show the parameter estimates and p-values for each predictor; different models are ordered from best to worst.
Each candidate model included 455 observations. Numbers indicate the parameter estimate for each variable included in a given model. Dependent variables (human WNV incidence rates and WNV-positive corvid death ratios) were log10+1 transformed, whereas independent variables were estimated over each census tract.
Akaike weights, ωi = exp(−1/2 ΔAIC) / ∑exp((−1/2 ΔAIC).
After including variables with p < 0.07 in the estimation of ∑ωi. Without including marginally significant variables, the sum of Akaike weights drop to 0.04.
p < 0.05;
p < 0.07.